石英砂表面活性滤膜去除地下水中氨氮的试验研究

为研究石英砂滤料表面活性滤膜催化氧化地下水中氨氮的性能,采用已运行4年的中试石英砂滤柱,改变进水氨氮负荷并且长期持续过滤仅含氨氮的进水,考察该滤膜催化氧化氨氮的性能.结果表明:在进水氨氮浓度为0.8~1.3mg/L,水温为20~23℃,滤速为7m/h的试验条件下,滤料表面活性滤膜催化氧化氨氮的性能可长期保持稳定、高效;在溶解氧(DO)充足的条件下,氨氮的最大去除负荷为22.3g/(m³·h),且其与氨氮进水负荷正相关;氨氮的极限去除浓度受溶解氧的限制,且当DO不足时,滤速对溶解氧的消耗影响较大.     

Environmental deterioration of farmlands caused by the irrational use of agricultural technologies

Without considering the ecosystem-dependence of agricultural production, irrational use of agricultural technologies could bring only short-term economic benefits but leave long-term environmental deterioration. If some agricultural lands have to be abandoned because of these technologies such as chemical films or groundwater depletion, it will aggravate the burden of remaining lands for maintaining or enhancing production. Thus, agricultural production should be a part of public services, requiring the consideration of interests of different stakeholders and sustainability.     

黄土高原半干旱区覆膜玉米土壤温度的变异特征

黄土高原半干旱丘陵山区受特殊的地理、地形以及水文气象条件的影响,造成农业生产播种难、出苗率低等问题,严重制约着农业的发展,但通过覆膜坐水技术能够起到抗旱保墒、提高地温、改善土壤肥效等作用。以哲单7号玉米ZeamaysL为供试品种,在设置对比试验小区（覆膜与不覆膜）的基础上,通过分析覆膜玉米土壤温度变异特征,描述了覆膜后增温、提墒、增产的过程,研究结果表明：覆膜处理与不覆膜处理相比,增温最明显的时期出现在出苗到拔节阶段,且10cm．和20cm处的温差表现为最大,可增温2．5℃左右,而后期增温减慢,播种后覆膜增温为玉米发芽生长提供了良好的生长环境,大大提高了出苗率,为作物节水增产提供了必要条件。     

Biosorption of Cr(III) from aqueous solution by freeze-dried activated sludge: Equilibrium,kinetic and thermodynamic studies

Batch biosorption experiments were conducted to remove Cr(III) from aqueous solutions using activated sludge from a sewage treatment plant. An investigation was conducted on the effects of the initial pH, contact time, temperature, and initial Cr(III) concentration in the biosorption process. The results revealed that the activated sludge exhibited the highest Cr(III) uptake capacity (120 mg·g⁻¹) at 45°C, initial pH of 4, and initial Cr(III) concentration of 100 mg·L⁻¹. The biosorption results obtained at various temperatures showed that the biosorption pattern accurately followed the Langmuir model. The calculated thermodynamic parameters, ΔG^o (−0.8– −4.58 kJ·mol⁻¹), ΔH^o (15.6–44.4 kJ·mol⁻¹), and ΔS^o (0.06–0.15 kJ·mol⁻¹·K⁻¹) clearly indicated that the biosorption process was feasible, spontaneous, endothermic, and physical. The pseudo first-order and second-order kinetic models were adopted to describe the experimental data, which revealed that the Cr(III) biosorption process conformed to the second-order rate expression and the biosorption rate constants decreased with increasing Cr(III) concentration. The analysis of the values of biosorption activation energy (E_a = −7 kJ·mol⁻¹) and the intra-particle diffusion model demonstrated that Cr(III) biosorption was film-diffusion-controlled.     

吉林省主要覆膜作物地膜残留情况调查

通过文献调研、问卷调查和典型样点采集的方法对吉林省3种主要覆膜作物的地膜残留情况进行调查分析,结果表明：地膜残留量与覆膜年限、地膜回收方式以及种植作物种类密切相关。随覆膜时间的延长地膜残留量有增加的趋势。3种模式地膜残留量由高到低为：瓜菜模式〉玉米连作模式〉花生连作模式,连续覆膜10年,3种模式的地膜残留量分别为30、28.35 kg·hm^-2和15.9kg·hm^-2。以一级污染水平作为标准（75 kg·hm^-2）,覆膜量每年按75～150 kg·hm^-2、年残留率按1.2%～4.02%计,估算吉林省安全使用地膜的年限约为12～83年。     

TiO2薄膜光催化体系中羟基自由基的水杨酸分子探针法测定

以水杨酸为分子探针物,以分光光度法测定了纳米TiO2薄膜光催化体系中产生的羟基自由基(·OH).结果表明,水杨酸的自然氧化程度较低,可以作为分子探针测定·OH的产生;实验中最佳的光照时间为60min;水杨酸浓度对·OH的测定影响较大,其最佳值为50 mg·L-1;pH值对·OH的测定影响较大,最佳值为6;最佳实验条件下,分析得到·OH的稳态浓度为1.68×10-14 mol·L-1.     

铸造废砂／废地膜／粘附土三元复合体系的研究

通过X射线衍射分析、红外光谱分析、热分析、电镜及能谱分析、图像分析,可以判断废旧地膜上粘附土的主要矿物质是结晶二氧化硅（粉粒级石英）,它们与聚合物基废弃物复合材料中作为填料的铸造石英砂的性状类同。废旧地膜可以不经清洗,直接与铸造废砂制备复合材料,这可大大降低复合材料的加工成本。这种复合材料实际上是由基体PE、粘附土中大量的SiO2和铸造石英砂SiO2组成的三元复合体系。     

地膜覆盖对稻-油轮作农田温室气体排放的影响

以位于西南大学农业部重庆紫色土生态环境重点野外科学观测试验站内的稻-油轮作为研究对象,采用静态箱/气相色谱法,对覆膜和对照(不覆膜)处理下稻油轮作CO2、CH4和N2O排放特征进行了为期1 a的原位观测.结果表明,稻-油轮作农田CO_2、CH_4和N_2O排放通量均呈现出明显的季节变化,且2种处理下这3种温室气体的季节变化模式相似.覆膜处理下稻-油轮作农田全年CH_4排放量为(46. 14±13. 40) kg·hm~(-2),相比于对照处理下的(18. 61±2. 05) kg·hm~(-2),提高了147. 93%(P 0. 05),但覆膜对CO_2和N_2O的排放影响并不显著,覆膜及对照处理下CO2年排放量分别是(-47. 54±2. 11) t·hm~(-2)和(-47. 60±2. 19) t·hm~(-2),N2O年排放量分别是(18. 94±4. 74) kg·hm~(-2)和(23. 14±3. 68) kg·hm~(-2).覆膜和对照处理下GWP值分别为-41. 16 t·hm~(-2)和-40. 95 t·hm~(-2),表现为大气温室气体的吸收汇,但差异并不显著.     

铝合金化学氧化膜盐雾试验后腐蚀点评定方法研究

目的制定飞机用2024铝合金表面阿洛丁1200S化学氧化膜盐雾试验后腐蚀点的评定依据。方法通过开展铝合金化学氧化膜盐雾试验,分别利用目视、SEM微观、能谱分析和电化学阻抗测试等手段,表征盐雾试验后的腐蚀形貌及特征。结果试验后样品表面出现的典型腐蚀特征尺寸大于或等于0.15 mm时,正常视力的检测人员均能目视可见。目视可见的黑点、典型彗星状拖尾或只有彗星尾巴等形貌处的化学转化膜和基材已腐蚀,局部有腐蚀点的膜层,其耐蚀性大幅下降,失去对侵蚀性介质的阻挡能力。结论仅出现不符合目视可见和基体腐蚀特征,不能判定为腐蚀点。当出现肉眼可见的黑点,典型彗星状拖尾或只有彗星尾巴等形貌,可判定为腐蚀点。在实际生产检验检测过程中,可采取类似方法研究腐蚀点的评判方法,建立铝合金表面处理盐雾试验后腐蚀图谱和腐蚀点评定准则。     

Effect of environmental parameters on the degradability of polymer films in laboratory-scale composting reactors

Previous research in our laboratory reported a convenient laboratory-scale composting test method to study the weight loss of polymer films in aerobic thermophilic (53°C) reactors maintained at a 60% moisture content. The laboratory-scale compost reactors contained the following synthetic compost mixture (percentage on dry-weight basis): tree leaves (45.0), shredded paper (16.5), food (6.7), meat (5.8), cow manure (17.5), sawdust (1.9), aluminum and steel shavings (2.4), glass beads (1.3), urea (1.9), and a compost seed (1.0) which is designated Mix-1 in this work. To simplify the laboratory-scale compost weight loss test method and better understand how compost mixture compositions and environmental parameters affect the rate of plastic degradation, a systematic variation of the synthetic mixture composition as well as the moisture content was carried out. Cellulose acetate (CA) with a degree of substitution (DS) value of 1.7 and cellophane films were chosen as test polymer substrates for this work. The extent of CA DS-1.7 and cellophane weight loss as a function of the exposure time remained unchanged when the metal and glass components of the mixture were excluded in Mix-2. Further study showed that large variations in the mixture composition such as the replacement of tree leaves, food, meat, and sawdust with steam-exploded wood and alfalfa (forming Mix-C) could be made with little or no change in the time dependence of CA DS-1.7 film weight loss. In contrast, substituting tree leaves, food, meat, cow manure, and sawdust with steam-exploded wood in combination with either Rabbit Choice (Mix-D) or starch and urea (Mix-E) resulted in a significant time increase (from 7 to 12 days) for the complete disappearance of CA DS-1.7 films. Interestingly, in this work no direct correlation was observed between the C/N ratio (which ranged from 13.9 to 61.4) and the CA DS-1.7 film weight loss. Decreasing moisture contents of the compost Mix-2 from 60 and 50 and 40% resulted in dramatic changes in polymer degradation such that CA DS-1.7 showed an increase in the time period for a complete disappearance of polymer films from 6 to 16 and 30 days, respectively.Guest Editor: Dr. Graham Swift, Rohm & Haas.Paper presented at the Bio/Environmentally Degradable Polymer Society—Second National Meeting, August 19–21, 1993, Chicago, Illinois.